100 likes | 336 Views
Experiences with Wet Test Methods for Formaldehyde. Rick Szekeres Environmental Chemist Pennsylvania Department of Environmental Protection http://www.dep.state.pa.us/dep/deputate/airwaste/aq/source/sts.htm. Brief History of Wet Test Methods. 1990 EPA Method (EPA/600/3-90/005)
E N D
Experiences with Wet Test Methods for Formaldehyde Rick Szekeres Environmental Chemist Pennsylvania Department of Environmental Protection http://www.dep.state.pa.us/dep/deputate/airwaste/aq/source/sts.htm
Brief History of Wet Test Methods • 1990 EPA Method (EPA/600/3-90/005) • Constant Rate Sampling; DNPH • 1991 BIF Method 0011 (SW-846) • Isokinetic Sampling; DNPH (opt. breakthrough check) • NCASI Chilled Impinger Methods • Constant Rate Sampling (400±50 cc/min); Water • CI/SG/PULP-94.02 (for pulp & paper mills) • No filter; 2 Impingers, first empty • CI/WP-98.01 (for wood products mills) • Hot probe/filter; two impingers • IM/CAN/WP-99.01 (for wood products mills) • Hot probe/filter; 3 Impingers, first with glass frit • EPA Method 301 Validation
Allegheny Particleboard Tests • 06/94 1990 EPA Method (constant rate) • 08/94 BIF Method 0011 (isokinetic) • Board Press & Cooler results were substantially lower • Why were the results so different? • Process Variability? • Difference in Sampling Rate? • Breakthrough, despite unreacted DNPH?
Yorktowne Department Tests • Waste Wood-Fired Boilers w/common stack • 5 MMBtu/hour heat input (per unit) • Cyclones used for particulate control • 07/96 BIF Method 0011 • 2 impingers, each with 150 mL of DNPH • 31.6% of CH2O in last impinger; probable breakthrough • 10/96 BIF Method 0011 • 4 impingers, each with 150 mL of DNPH • 0.1% of CH2O in last impinger; no breakthrough • Mass emission rate was 2.7x higher • CH2O emissions much higher than AP-42 Factor • 2 lbs/ton versus 0.019 lbs/ton (assuming HHV of 8500 btu/lb)
Wood-Mode Department Tests • Virgin or Waste Wood-Fired Boiler • 30MMBtu/hour heat input • Cyclone used for particulate control • 08/96 BIF Method 0011 • 4 impingers, each with 150 mL of DNPH • 0.1% of CH2O in last impinger; no breakthrough • Fuel had no appreciable impact on CH2O emissions • Some aldehyde emissions increased for waste wood • CH2O emissions much higher than AP-42 Factor • 5 lbs/ton versus 0.019 lbs/ton (assuming HHV of 8500 btu/lb)
Testing at MDF Plants(BIF Method 0011) • 10/97 Allegheny MDF • 57.3% of formaldehyde in last (2nd) impinger • Probable breakthrough • 11/97 MacMillan Bloedel Clarion • 4.4% of formaldehyde in last (3rd) impinger • No breakthrough
Testing at MDF Plants(NCASI Method CI/WP-98.01) • 12/98 Masonite Corporation • 2-58% of formaldehyde in last (2nd) impinger • 10% for Die Form Press • 38% for Resin Blender • 46% for Felter Scrubber • 58% for Board Cooler • 46% for First Stage Dryer • 2% for Second Stage Dryer • Probable breakthrough when sampled at 650 cc/min
Testing at MDF Plants(Method 25C vs. Method 25A) • Misreporting or Underreporting • Non-Simultaneous Testing at Two Facilities with Similar Production Capacity • Results from one facility appeared to be twice as high as from the other facility • Why were the results so different? • Reporting Issues • Differences in Operating Conditions
Issues of Concern • Do the various test methods produce data that is comparable? • If the test methods are not comparable, how does one decide which procedure is appropriate? • Is breakthrough a problem? • Is formaldehyde being accounted for? • Would audit samples help validate the data?